Water Demand Management versus Water Supply Policy: the Ebro River Water Transfer José Albiac Unidad de Economía Agraria Servicio de Investigación Agroalimentaria.

Slides:



Advertisements
Similar presentations
Reporting sheet no.3 State and quantity of water resources.
Advertisements

Islands for equal chances How can EU policies help filling the gap? Balearic Islands (ES) Corsica (FR) Sicily (IT) Sardinia (IT) Crete (GR) South Aegean.
International Economics Tenth Edition
International Economics Tenth Edition
International Trade Policy
Effects of Agricultural Commodity Programs Kristin Mackie & Lane Mayberry.
Agricultural Land Use Lori Lynch, Professor Agricultural and Resource Economics University of Maryland.
The Management of Water and Land Resources for Agriculture in Chinese Taipei Ho, Yi-Fong Wu, Chii-Reid Asia-Pacific Economic Cooperation APEC International.
Background: Land scarcity and fragmentation Arable land of China is only 10% of the total arable land of the World (World Bank data and projections) Population.
Fluctuation in Rainfall Variance in rainfall in Singapore.
Should Governments Subsidise Food Prices? To see more of our products visit our website at Neil Folland.
Derek Eaton Division of Technology, Industry & Economics Economics & Trade Branch Geneva, Switzerland “Designing the Green Economy” Centre for International.
Agricultural and Policy Development in China Agricultural and Policy Development in China Dr. Ke Bingsheng Director-General Research Center for Rural Economy,
PRIMARY SECTOR UNIT TWO.
The Drought Crisis and Impact in Agriculture
The European Union Water Framework Directive (WFD) requires member states to balance ecological and economic water management objectives in water resources.
Climate change impact on water resources Comoro islands are located in the Western Indian Ocean about 10 degrees south of the Equator and less than 300.
Jordan River Rehabilitation Project March 22 nd /6/20151.
Pollution under Spanish and European Policies Thirteenth Annual Conference EAERE Budapest, June 25-28th 2004 Agricultural Pollution Control under Spanish.
The 8-7 National Poverty Reduction Program in China: the National Strategy and its Impact Wang Sangui, Li Zhou, Ren Yanshun.
Chapter 13. The Economics of Water The Value of Water Water as a Public versus a Private Good Water Affordability Water Marketing Water Banking Pollution.
Sample Questions ECON 2420 Exam 1.
PRACTICE FROM CHINA GEF HAI BASIN INTEGRATED WATER AND ENVIRONMENT MANAGEMENT PROJECT World Bank / Liping Jiang In Cairns 23/10/2009.
Capacity Building in Analytical Tools for Estimating and Comparing Costs and Benefits of Adaptation Projects in the Berg River Basin, South Africa AIACC.
Water resources management in the island of Crete: present situation, problems and perspectives NAGREF, Institute for Olive Tree and Subtropical Plants,
WATER ISSUES IN THE EASTERN EUROPE:
Universidad de Zaragoza Servicio de Investigación Agroalimentaria 1 ECONOMIC ANALYSIS OF THE EBRO WATER TRANSFER José Albiac Servicio de Investigación.
EU, SIXTH FRAMEWORK PROGRAMME Optimisation for Sustainable Water Management EU funded Project: OPTIMA INCO-MPC Partner: INTERGEO Environmental Technology.
Upali Amarasinghe IWMI Delhi
An Analysis of the Pollutant Loads and Hydrological Condition for Water Quality Improvement for the Weihe River For implementing water resources management.
1 Sustainable Agricultural Economic benefits of reservoir scale expansion in Balkh Basin, Afghanistan Abdelaziz A. Gohar & Frank A. Ward New Mexico State.
Challenges for the corn supply chain in Brazil: from investments in logistics infrastructure to regulation of biotechnology Profa. Dra. Andréa Leda R.
Water Stress in China: Shortage and Pollution CHEN Ying Research Centre for Sustainable Development (RCSD) Chinese Academy of Social Sciences (CASS) CASS-Nottingham.
Chapter 23 – Policies that lower the price of food by increasing supply.
Chapter 21: How We Obtain and Use Water. Water To understand water, we must understand its characteristics, and roles: –Water has a high capacity to absorb.
Market Failures and Abiotic Resources. Review Fund-service vs. stock-flow resources Rival, non-rival but congestible, non-rival, anti-rival What’s the.
Introduction A GENERAL MODEL OF SYSTEM OPTIMIZATION.
CLIMATE CHANGE AND WATER MAKING RIVER BASIN MANAGEMENT PLANS “CLIMATE PROOF” IN SPAIN.
Water scarcity in the Arab world: how to get from ‘crisis’ to ‘sustainable’? Rania el Masri, Ph.D. Environment and Energy Policy Specialist Cairo, May.
WATER SCARCITY. Water stress and Water scarcity occur when the demand for water exceeds the available amount during a certain period or when poor quality.
How feasible is it to obtain water supplies by desalination? By Adam, James and Liam.
INTEGRATED WATER RESOURCES MANAGEMENT IN HAI BASIN OF CHINA BY LIPING JIANG WORLD BANK OFFICE BEIJING PRESENTED IN THE WORLD BANK WATER WEEK FEBRUARY 17-19,
NATIONAL WATER RESOURCE STRATEGY SOUTH AFRICA’S WATER SITUATION AND STRATEGIES TO BALANCE SUPPLY AND DEMAND LOWER VAAL WMA.
NATIONAL WATER RESOURCE STRATEGY SOUTH AFRICA’S WATER SITUATION AND STRATEGIES TO BALANCE SUPPLY AND DEMAND LOWER ORANGE WMA.
The government of an importing country wants to introduce a policy to support the incomes of its farmers. It is considering making the choice between three.
DESALINATION AT THE SPANISH MEDITERRANEAN BASIN CARLOS MASSA ACUAMED’S General Director March 20th 2009.
Ecologic.eu Brussels, 19 March 2009 Environmental & economic impact of water pricing and quotas in the agriculture sector What do we learn from practical.
Lesson 1 Identifying Environmental and Economic Impacts from Soil Erosion.
Water Resources in the Indus-Gangetic Basin
Introduction to Economics of Water Resources. Public or private Excludability (E): the degree to which users can be excluded Subtractability (S): the.
BASIN SCALE WATER INFRASTRUCTURE INVESTMENT EVALUATION CONSIDERING CLIMATE RISK Yasir Kaheil Upmanu Lall C OLUMBIA W ATER C ENTER : Global Water Sustainability.
California Water Briefing APRIL 2006 Department of Water Resources.
 The Future of Water Conflicts. What can you think of?  What factors can you think of that will affect the future water security of different countries?
Water buyback in Spain: what can we expect? AARES 60 th Annual Conference 2-5 February 2016, Canberra, Australia C. D. Pérez-Blanco, FEEM & CMCC.
International Economics International Economics Tenth Edition Trade Restrictions: Tariffs Dominick Salvatore John Wiley & Sons, Inc. Salvatore: International.
Climate Change Impacts on Water Resources and Human Livelihoods in the Coastal Zones of Small Island Developing States (CASCADE) Project Stakeholder Panel.
Modeling with WEAP University of Utah Hydroinformatics - Fall 2015.
Ratio Analysis…. Types of ratios…  Performance Ratios: Return on capital employed. (Income Statement and Balance Sheet) Gross profit margin (Income Statement)
Water Management in Spain Teodoro Estrela Júcar River Basin Authority, Spain.
Water Charge Instruments for Environmental Management in Latin America: from Theoretical to Practical Issues Mexico Country Case Lilian SAADE HAZIN and.
Water Reforms Across the World: Policy and Technological Innovations
Copyright © 2013 Jonathan M. Harris
The Importance of Transportation Economics
IMPLEMENTATION OF ARTICLE 9
Contents Ecological effects (Beijing City)
20/05/2019 GROUNDWATER MANAGEMENT IN DROUGHT PERIODS. Vienna. October the 8th, 2018 M. Carmen Montoro Cavero. Water Commisariat. Confederación Hidrográfica.
SEGURA PRB Water Exploitation Index+ (WEI+)
The Importance of Transportation Economics
Optimization for Sustainable Water Resources
Water Use in Agriculture ● 2009 EEA Report ● SoE-WISE Reporting ● Water Accounts
Presentation transcript:

Water Demand Management versus Water Supply Policy: the Ebro River Water Transfer José Albiac Unidad de Economía Agraria Servicio de Investigación Agroalimentaria Water Forum 2002 Inter-Basin Transfers May 6-8, 2002 Demand Management and Transfer

Irrigation in Spain Spain is a country with a land surface of 506,000 km 2 and annual precipitations around hm 3 (684 mm), with large spatial and temporal rainfall variation. Total river flow is 110,100 hm 3, with a water storage capacity of 56,100 hm 3, and an average storage around 25,000 hm 3. Demand Management and Transfer

Water demand for consumptive uses reaches almost 30,400 hm 3, divided between 24,100 hm 3 for agricultural uses and 6,300 hm 3 for urban and industrial consumption. New urban and industrial demands and the emergence of environmental concerns related to water provision and usage are creating pressures to introduce new water management policies. Demand Management and Transfer

In the present scenario of water scarcity, the assignment of water among competing uses has created strong conflicts among user groups and regional governments. The water scarcity is specially acute in the Southeastern watersheds, because the expansion of fruit and vegetable production has created a huge demand for water, triggering over-exploitation of aquifers and degradation of hidric systems. Large investments are proposed by the National Hydrologic Plan to transfer water from the Ebro basin to the Southeastern basins (6 billion €). Demand Management and Transfer

Irrigated area in Spain reaches 3.43 million ha, distributed between 2.31 million ha of arable crops and 0.84 millions of tree crops. Cereals fill 967,000 ha generating an income of 914 million € (1€ = 0.89 US$) “Industrial” crops fill 569,000 ha with 932 million € of income Vegetables area is 357,000 ha generating an income of 3,720 million € Citric and non-citric fruit trees fill 501,000 ha and generate 2,482 million €. Demand Management and Transfer

Cereals and “industrial” crops have an average income per cubic meter much lower than fruits and vegetables: 0.12 €/m 3 for cereals 1.64 €/m 3 for vegetables and 0.84 €/m 3 for fruit trees. Demand Management and Transfer

Cereal in Aragón Donating Ebro basin Demand Management and Transfer

Vegetables in Murcia and Almería Receiving Segura and South basins

Demand Management and Transfer Crop costs and margins in €/ha Yield (kg/ha) IncomeDirect costs Machinery and salary costs Indirect and amortization costs Net margin Corn9,5001, Barley3, Tomato83,000 25,876 1, , Greenhouse tomato 125,000 38,970 4,574 1,934 1,905 30,558 Broccoli26,500 10,352 2,208 1, ,686 Orange26,000 5,546 1, ,113 2,136

Fruits and vegetables are highly profitable crops and a large share of production is located in the southeast where over-exploitation of water resources is severe. The Ministry of Environment indicated in the White Book on Water that in the future the administration will support irrigation areas with high economic profits, but not the low profit irrigated areas of the interior Spain, and the Ebro water transfer is the result of this policy. Demand Management and Transfer

Questions examined Study on water demand management and supply policy The analysis of water demand in the Levante counties shows that a demand management policy with higher prices solves water scarcity, without need for external transfers which would deteriorate the ecological functionality of the Ebro source basin and prolong the current unsustainability of the Júcar, Segura and Sur receiving basins. The study considers water demand management as an alternative to the supply policy of the Ebro water transfer, proposed by the Spanish National Hydrologic Plan. Demand Management and Transfer

Questions examined

Scenarios considered In the first scenario, a strategy is analyzed in which aquifer overexploitation is prohibited, and there are no transfers of water from other basins. The effects on the agricultural sector of alternative solutions to water scarcity, have been examined by two demand management scenarios: In the second scenario, a price raise is considered in order to calculate the price of water that balances the global water demand placed on the basins of Levante with the available water resources of those basins. Questions examined Demand Management and Transfer

The analysis of the impact of alternative solutions to the water scarcity in Levante shows that the ban on aquifer overexploitation as a strategy of demand management without external transfers of water causes a fall of 20 percent in the final agricultural production and net profit in the Levante basins. This alternative would be especially damaging for Almería, while the negative effects would be less in Segura and Júcar. The extent of the impact of this alternative depends on the reassignment of water among the zones where there is scarcity. The ban on overexploitation ofaquifers would be very negative for Almería Elimination of overexploitation Demand Management and Transfer

Location of losses The counties that have the greatest losses in Almería are those which have very profitable crops, and in Segura those which bear the greatest reduction of available water: Campo Dalias, Bajo Almanzora and Campo Níjar- Bajo Andarax in Almería, and Valle del Guadalentín and Nordeste in Murcia. In Campo Dalias income and net income fall 378 and 180 million €, and in Valle del Guadalentín they fall 103 and 44 million €, respectively. Nearly 70 percent of the losses of net profit, that’s 204 million € of 306 in losses, occur in Almería (South basin) Elimination of overexploitation Demand Management and Transfer

Almería Campo Dalias Bajo Almanzora Campo Níjar-Bajo Andarax Murcia Valle del Guadalentín Nordeste Elimination of overexploitation

Even if the proposed transfer is carried out, the overexploitation of aquifers in Almería will not be solved. In any case, to solve this problem it will be necessary to introduce additional measures of demand management that rebalance availabilities and uses. The water allocation envisaged by the NHP to solve aquifer overexploitation in the South basin is only 58 hm 3, which is insufficient to avoid the current overexploitation that reaches 71 hm 3. In contrast, the quantities proposed by the NHP for transfers into the Júcar and Segura basins are much more generous. Elimination of overexploitation Demand Management and Transfer

The alternative of increasing the price of irrigation water balances the global supply and demand for water in the Levante basins, and follows the criteria of the Water Framework Directive. Water prices for agricultural use can continue to be less than those for other uses, but there should be a reasonable increase in prices, which frees up water resources, with an impact not excessive for farmers. This demand management policy is preferable for society, as it has a lower economic and environmental cost than the policy of expanding the supply through transfers from the Ebro Valley. Demand management avoids scarcity with a much lower economic and environmental cost than the water transfer project Price increases Demand Management and Transfer

An increase of 0.12 €/m 3 reduces the size of the water project to 379 hm 3 with a cost to farmers of 294 million € net annual income, which measures the compensation that could be offered by the administration or by other water users, so that the farmers voluntarily accept the raise in water prices. The regional (state) administrations of the conceding basin should negotiate this alternative with the central government, an alternative which reduces the size of the water transfer to Levante from 820 to 379 hm 3. Price increases Demand Management and Transfer

The action of raising prices 0.18 €/m 3 should be seriously considered by public administration heads, political groups and lobbyists as an alternative to the enormous investment in the Ebro water transfer project. An increase of 0.18 €/m 3 eliminates water scarcity in Levante at a cost of 423 million € for farmers, remaining only a deficit of 68 hm 3 in Segura and 49 hm 3 in South, which could be resolved employing desalinization and improving irrigation efficiency. Price increases Demand Management and Transfer

The cost is substantial for farmers, and the necessary compensation so that Levante farmers voluntarily accept the raise in prices is 423 million €, equal to their net annual income loss. This amount could be paid by the administration and other water use groups, so that the society doesn’t carry out the investment of more than 6 billion €. This money could be designated to alternative investments having greater profitability. Price increases Demand Management and Transfer

NHP inconsistency Severe problem of inconsistency in the Segura basin The diverted water will have high costs in the range 0,19-0,75 €/m 3 depending on the county, well above the low price that farmers pay now, and this elevated water price will only pay for itself in counties with high profit crops. The volume of diverted water that the Levante counties can absorb at this price is 863 hm 3 in Júcar, 215 hm 3 in Segura and 112 hm 3 in South. These quantities should be compared with the water allocations for agricultural and environmental use by NHP, which are 141 hm 3 in Júcar, 362 hm 3 in Segura and 58 hm 3 in South. Demand Management and Transfer

Thus, in the Segura basin there is a significant problem of inconsistency in the NHP proposed transfer, since this basin can only absorb 220 hm 3 of water destined to agricultural use at the water transfer prices, which does not cover the NHP assignment of 362 hm 3 designated to end the overexploitation of aquifers and to meet the irrigation guarantee. NHP inconsistency Demand Management and Transfer

Effective water demand, compared with the volume of over- exploitation and irrigation guarantee NHP inconsistency

Transfer subsidy Subsidy of transferred water is feasible, but very costly for nonagricultural users in Segura. In Segura, if a surcharge is placed on the actual urban and industrial water usage in the Murcia region (plus the transfer allotment), in order to subsidize in €/m 3 the allocation for agricultural and environmental use, the surcharge will reach 0.68 €/m 3. The resulting price for urban and industrial users would be about 1.59 €/m 3, similar to the price paid in the Canary Islands. Demand Management and Transfer